Current through Register Vol. 18, September 20, 2024
(1) The
department shall participate in recovery efforts of threatened and endangered
plant and animal species as listed below. The department shall confer in its
sole discretion with the United States Fish and Wildlife Service (USFWS) to
develop habitat mitigation measures.
(a)
Measures may differ from federal management guidelines because the department
plays a subsidiary role to federal agencies in species recovery. In all cases,
measures to support recovery must be consistent with department
responsibilities under the Endangered Species Act and Trust Law. The department
shall work with the USFWS to amend such measures when, in the judgment of the
forest management bureau chief, they are inconsistent with trust management
obligations.
(b) Measures to
support species recovery shall be periodically updated to implement new
biological information and legal interpretations as warranted.
(2) The department shall, in its
sole discretion, participate on interagency working groups established to
develop guidelines and implement recovery plans for threatened and endangered
species.
(a) If additional plant or animal
species with habitat on state trust lands are federally listed as threatened or
endangered, the department shall, in its sole discretion, participate in
working groups for those species.
(b) The department shall, in its sole
discretion, also participate in interagency groups formed to oversee management
of recently de-listed species.
(3) The department staff shall report
sightings of threatened and endangered species to respective working groups or
an appropriate data repository.
(4)
With respect to Canada lynx, the department will:
(a) establish and maintain a lynx habitat map
utilizing science-based habitat classifications, which may be revised and/or
replaced based on improved scientific information upon approval of the forest
management bureau chief, including:
(i)
summer foraging habitat;
(ii)
winter foraging habitat;
(iii)
other suitable habitat;
(iv)
temporary non-suitable habitat; and
(v) total potential habitat;
(b) commit to the following
project-level measures in mapped lynx habitat to provide downed woody structure
for lynx escape cover, habitat for prey species, and structure that may provide
some potential den sites in the future by:
(i) providing for retention of coarse woody
debris using applicable scientific publications;
(ii) emphasizing the retention of downed logs
of 15-inch diameter or larger where they occur, and managing to retain at least
one large log per acre that is at least 20 feet long; however
(iii) retention of coarse woody debris may be
superseded in special management situations where other goals must be
considered such as:
(A) fuels management and
aesthetic considerations in the urban interface;
(B) projects near recreational areas, where
downed wood is collected and burned;
(C) harvest units adjacent to open
roads;
(D) broadcast burning;
and
(E) meeting mandated hazard
reduction requirements; but
(iv) ensuring adequate recruitment for Canada
lynx, by retaining an average of two snags and two live snag recruitment trees
of greater than 21 inches diameter at breast height (DBH) per acre in stands
identified as lynx habitat:
(A) if snags or
snag recruitment trees of greater than 21 inches DBH are not present, then the
largest snags or snag recruitment trees available will be retained;
(B) snags may be evenly distributed or
clumped, but if there is an absence of sufficient snags or recruits, some
substitution between the two may occur;
(v) leaving one percent of the definable
blowdown area unsalvaged on blowdown salvage projects involving flattened
patches, where the material will be retained in a nonlinear patch or patches to
the extent practicable;
(c) prohibit motorized forest management
activities and prescribed burning associated with forest management activities
within 0.25 mile of known active lynx den sites from May 1 through July 15;
(d) proceed with suspended
activities if a department biologist has confirmed that lynx have vacated the
den site vicinity prior to July 15;
(e) retain small, shade-tolerant trees
including grand fir, subalpine fir, and Engelmann spruce in thinned portions of
pre-commercial thinning units within mapped lynx habitat that do not pose
substantial competition risks to desired crop trees;
(f) retain patches of advanced regeneration
of grand fir, subalpine fir, and Engelmann spruce as a component of commercial
harvest prescriptions in winter foraging habitat, where canopy cover of
retained patches would typically not exceed ten percent of the stand area
through implementation of this measure;
(g) design harvest units to maintain a
connected network of suitable lynx habitat along RMZs, ridge tops, and saddles
on timber sale projects;
(h)
document in MEPA analysis the circumstances where maintaining habitat
connectivity and travel corridors along ridge tops and saddles are
impracticable, which may include:
(i)
non-forested ridges;
(ii)
non-forested saddles;
(iii)
harvest units where cable systems are used;
(iv) locations where habitat associated with
scattered parcels is isolated by management on surrounding ownerships;
(v) locations where lynx habitat
polygons are isolated within a parcel;
(vi) locations where forest types not
preferred by lynx bisect lynx habitat;
(vii) locations where silvicultural,
fiduciary, or access objectives cannot be met;
(viii) lodgepole pine stands requiring
stand-replacement harvest; and
(ix) retaining trees on sites with high
potential for blowdown;
(i) implement the following on total
potential lynx habitat on scattered parcels outside of LMAs:
(i) maintain at least 65 percent of total
potential lynx habitat as suitable habitat at the land office scale;
and
(ii) maintain no more than 35
percent as temporary non-suitable habitat at the land office scale;
(j) implement the following on
defined LMAs:
(i) maintain at least 65 percent
of total potential lynx habitat as suitable lynx habitat, and no more than 35
percent as temporary non-suitable habitat;
(ii) prohibit conversion of more than 15
percent of the total potential lynx habitat to temporary non-suitable habitat
per decade within each lynx management area;
(iii) maintain at least 20 percent of total
potential lynx habitat as winter foraging habitat;
(iv) identify and retain un-thinned 20
percent of each pre-commercial thinning project area in lynx habitat, where:
(A) patches will maintain a density of
greater than 2,000 stems per acre;
(B) in stands where a density of 2,000 stems
per acre is not present, areas will be retained with the greatest density
available;
(C) retention patches
will be designed to be at least five acres when possible to facilitate tracking
and promote habitat function;
(D)
retention patches of dense saplings will:
(I)
emphasize retention of subalpine fir, Engelmann spruce, and/or grand fir, where
available;
(II) locate retention
patches adjacent to other suitable lynx habitat where practicable;
and
(III) prohibit entry into
retention patches for future pre-commercial thinning or commercial harvest
until they structurally meet the department's minimum definition of
sawtimber.
AUTH:
77-1-202,
77-1-209,
77-5-201,
77-5-204,
MCA; IMP:
77-5-116,
77-5-204,
77-5-206,
77-5-207,
MCA